Environmental Geochemistry, GLY 4241/5243, © David Warburton, 2015 LECTURE 15 Petroleum and the Environment - Part 2 Note: Slide numbers refer to the PowerPoint presentation which accompanies the lecture. Petroleum 1, slide 1 here INTRODUCTION Petroleum 1, slide 2 here The use of petroleum and its derivatives represents a massive threat to the environment. Petroleum is used in huge quantities, and the use of petroleum has been increasing very rapidly, as Table 15-1 shows. Table 15 - 1 Petroleum Consumption, 1960 - 2005 Year Consumption, millions of barrels per day United States China World 1960 9.80 0.17 21.34 1965 11.51 0.25 31.14 1970 14.70 0.62 46.81 1975 16.32 1.36 56.20 1980 17.06 1.77 63.11 1985 15.73 1.89 60.09 1990 16.99 2.30 66.55 1995 17.72 3.36 69.91 2000 19.70 4.80 76.69 2005 20.80 6.72 83.65 2010 19.14a 8.23a 87.82a 2015 19.40a 11.97 95.01a Sources: 1960-1979—Energy Information Administration (EIA), International Energy Database. 1980 forward—EIA, "International Energy Annual 2009" (March 2009). From table 11.10 on the Energy Information Administration, 2009 BP Statistical Review of World Energy, 2016 a World petroleum consumption quadrupled from 1960 to 2008. Petroleum 1, slide 3 here 1 Environmental Geochemistry, GLY 4241/5243, © David Warburton, 2015 Starting in 2008, the world entered a deep recession, and oil consumption slowed in 2009. The United States is the leading petroleum consuming country. Chinese consumption has increased much faster than the rest of the world. Oil consumption in China is expected to increase 4 percent a year, and by 2025 China is projected to be the second largest oil consuming country in the world, accounting for 11 percent of total world consumption. During the period 1980 - 1995, United States consumption hardly increased. Since 2005, U.S. annual consumption has dropped. (Hirsch et al., 2005) As the projection on the graph from 2006 shows, the developing world, lead by China, has been increasing consumption very rapidly. Countries grouped as “Other” in the figure, including India, Mexico, and Brazil, were expected to experience oil consumption growth rates 10 to 30 percent higher than the world average. In 2015, China’s consumption rose 6.3%, India’s decreased 3.2%, Brazil decreased 4.2%, Mexico decreased 1.1%, and the United States increased 1.6%. As a whole, Europe Union rose 1.5%, Africa 3.2%, and Asia Pacific (includes China) rose 4.1%. ( B.P. Statistical Review, 2016). Petroleum 1, slide 4 here In 2013, global oil production increased by 557,000 barrels per day (bpd), reaching a new all-time high of 86.8 million bpd. Despite increasing consumption, production increased only 0.6 percent over 2012. After declining in 2009, global crude oil production increased 4 years in a row. U.S. production increase was 1.1 million bpd, while global oil global production declined by 554,000 bpd. (Rapier, 2014). The U.S. gain in oil production was the largest year over year gain for any country in 2013, and the largest gain in US history. The United Arab Emirates had second-largest increase with a gain of 248,000 bpd over 2012, and Canada increased 208,000 bpd over 2012, the only three countries in the world to record an increase of more than 200,000 bpd. As the graph shows, U.S. conventional oil production was on a steady decrease from 1984-2007, when fracking output kicked in. US Oil production has been at near record levels reaching 293,617 barrels in May, 2015 (record is 310,320 barrels in November, 1970) in the past couple of years. (U.S. Energy Information Administration, 2016). Petroleum 1, slide 5 here At any point while using petroleum, from drilling to final consumption, problems can develop. Petroleum may be released into the environment. Petroleum-derived hydrocarbons and chlorinated solvents are the most common contaminants of ground water (Averett and McKnight, 1988). Most often the release is accidental, through carelessness, poor design, or shear bad luck. Accidents may happen during shipping, such as the Torrey Canyon and Exxon Valdez spills, or through leakage at offshore facilities such as the Santa Barbara channel incident. Pipeline ruptures on land have produced large terrestrial spills. Sometimes the release is deliberate, as in the destruction of the oil fields in Kuwait or in cleaning and flushing of fuel tanks by ships and the discharge of the flush into the ocean. Occasionally, oil spills are the result of natural leakage. Whatever their origin, petroleum spills represent local to regional environmental problems, often of considerable severity. The cost of cleaning up petroleum contamination is usually very high, and the results of the cleanup are problematic. 2 Environmental Geochemistry, GLY 4241/5243, © David Warburton, 2015 Petroleum 1, slide 6 here Petroleum is a complex mixture. It contains a great variety of organic compounds. Petroleum from different sources has different compositions and different properties. Petroleum 1, slide 7 here The environmental problems generated by petroleum spills will depend a great deal on the original composition of the petroleum. Cleanup efforts need to done in accord with the nature of the material spilled. Refined petroleum products, such as gasoline, diesel fuel, jet fuel, home heating oil, etc. present problems that are much different from that of petroleum. Cleanup procedures need to be developed and applied for each derivative. Considering the tremendous environmental risks associated with the use of petroleum, phasing out all use of the substance quickly might seem prudent. Unfortunately the use of oil is a critical part of the energy infrastructure of all developed nations, and is often a crucial part of the infrastructure of less developed countries. If the spigot were turned off, incredible social and economic devastation would quickly follow. The problems associated with the naturally enforced phase out of petroleum as supplies are exhausted will be traumatic enough. Petroleum 1, slide 8 here THE CHEMISTRY OF PETROLEUM Petroleum is composed of many organic compounds, more than 75% of which are hydrocarbons. Hydrocarbons are composed of hydrogen and carbon. Organic compounds are, in principle, created by living organisms. In petroleum, some organic compounds may result from metamorphosis of organic matter. The fantastic number and variety of organic compounds are the result of the chemistry of carbon itself. Petroleum 1, slide 9 here Carbon atoms are small and possess four valence electrons. This means that carbon can form bonds with up to four other atoms. Generally these bonds are covalent, involving the sharing of electrons between atoms. The possibility of double bonds, involving the sharing of two electrons, and triple bonds, involving the sharing of three electrons, also exist. Carbon compounds may also form ring structures, where the head and tail of a carbon chain are bonded together. Other compounds may also be associated with petroleum. Petroleum 1, slide 10 here These compounds, which usually contain hydrogen and carbon, also contain other elements such as sulfur, nitrogen, or oxygen. Other atoms may range from trace amounts up to 4% sulfur, 1% 3 Environmental Geochemistry, GLY 4241/5243, © David Warburton, 2015 nitrogen, and lesser amounts of oxygen (Hunt and O'Neal, 1966). Small amounts of metals may also be presence. Metal amounts are generally in the parts per million range. The range for crude oil from California, Kansas, Texas, Kuwait and Morocco for various metals was iron, none to 31 ppm, nickel, 0.8 to 46 ppm, vanadium, 0.6 to 49 ppm, and copper, 0.1 to 1.1 ppm (Horne, 1978). Petroleum is usually described as groups of compounds. Each group has similar properties. This approach has great practical value in that it allows us to consider a very complex mixture as a few groups. The names given to these groups also simplify the discussion. Nevertheless, it must be realized that differences between compounds within the group do exist, and that these differences may be quite significant from an environmental perspective. Petroleum 1, slide 11 here Hydrocarbon properties vary regularly with increasing molecular weight. As molecular weight increases, the melting point, boiling point, and density of the compound increase. This is true also of many other related organic compounds. Petroleum 1, slide 12 here Petroleum is often conceptually divided into ?fractions” based on the number of carbon atoms in the compounds or on boiling point. As the result of the relationship between molecular weight and boiling point, the two schemes are nearly identical. Petroleum 1, slide 13 here Natural gas, often associated with petroleum, contains one to four carbon atoms (C1 to C4). The compounds from C6 to C10 makes up the gasoline fraction. Kerosene is composed of C10 to C16 compounds. C17 to C22 compounds make up lubricating oils and petroleum jelly. Those C22 and C29 are often called tar or asphalt (Krauskopf, 1979). Petroleum 1, slide 14 here The video demonstrates some of the properties of petroleum and shows how it can be distilled. Petroleum 1, slide 15 here Table 15 - 2 summarizes the properties of a few selected normal alkane hydrocarbons of different carbon number. 4 Environmental Geochemistry, GLY 4241/5243, © David Warburton, 2015 Table 15 - 2 Physical properties of selected normal alkanes FORMULA NAME FREEZING POINT, C BOILING POINT, C DENSITY, G/CM3 CH4 Methane -182 -161 Gas C2H6 Ethane -183 -89 Gas C3H8 Propane -190 -45 Gas C4H10 Butane -138 -1 Gas C5H12 Pentane -130 36 0.626 C6H14 Hexane -95 68 0.659 C7H16 Heptane -90 98 0.684 C8H18 Octane -57 125 0.703 C9H20 Nonane -51 151 0.718 C10H22 Decane -30 174 0.747 C11H24 Undecane -27 195 0.740 C16H34 Hexadecane 18 287 0.773 After Krauskopf, 1979, p.232 Petroleum 1, slide 16 here Hydrocarbons may also be classified by structural properties. One classification scheme breaks petroleum hydrocarbons into paraffins, cycloparaffins, aromatics, naphtheno-aromatics and residual fractions. Petroleum 1, slide 17 here Paraffins, also called alkanes, are split into normal paraffins and isoparaffins. A normal paraffin is a linear chain of carbon atoms. Each carbon atom in the interior of the chain is bonded to exactly two other carbon atoms. Paraffins make up about 25% of crude petroleum. They are usually in the low boiling (40 - 230C) fractions. Petroleum 1, slide 18 here An isoparaffin consists of a straight chain of carbon atoms with at least one branch. At the branch, one carbon atom is bonded to three other carbon atoms. Multiple branches off the 5 Environmental Geochemistry, GLY 4241/5243, © David Warburton, 2015 straight chain, or branches off branches, are possible. The dominant isoparaffins are the ones with the fewest and simplest branches. Petroleum 1, slide 19 here Cycloparaffins are also known as cycloalkanes or naphthenes. They are ring structures such as cyclohexane or 3,3,o-bicyclo-octane. Alkyl side-chains attached to the ring are common. An example is 1,2-dimethylcyclopentane. Cycloparaffins make up 30-60% of crude petroleum. The most common cycloparaffins have a single ring, generally with five or six carbon atoms (cyclopentane or cyclohexane). Compounds with up to six rings are common, and structures with up to ten rings may be found in high-boiling fractions (Stoker and Seager, 1977). Petroleum 1, slide 20 here Aromatic hydrocarbons are also cyclic. The aromatic hydrocarbons have delocalized electrons shared around the rings. These delocalized electrons make the bonds stronger than single bonds, but less than true double bonds. Benzene is the simplest aromatic hydrocarbon. Petroleum 1, slide 21 here Benzene and its derivatives are the most common aromatic hydrocarbons in the low-boiling fractions. Poly-cyclic aromatics are less common, and are found in higher-boiling fractions. Aromatic hydrocarbons are less common than paraffins or cycloparaffins in most crude petroleum. Petroleum 1, slide 22 here Naphtheno-aromatics, also called cycloalkanoaromatics, are combinations of the first three types. They are found in the higher boiling fractions (generally around 300C). Petroleum 1, slide 23 here The structure is usually a fusion of an aromatic and a cycloparaffin ring, often with paraffins present as alkyl branches. Petroleum 1, slide 24 here The residual fraction is composed of all types of high-boiling hydrocarbons, and the composition of most of these compounds is not known. It is known that these compounds often contain sulfur, nitrogen, oxygen, and trace metals. The compounds are often heterocyclic, with rings of both the cycloparaffin and aromatic type. Heterocyclic rings may be connected by short normal paraffin chains. A summary of the composition of crude petroleum by the classes is shown in Table 15 - 3. 6 Environmental Geochemistry, GLY 4241/5243, © David Warburton, 2015 Petroleum 1, slide 25 here Table 15 - 3 Petroleum Composition by Fraction Fraction Description Number of Carbon Atoms Crude Petroleum (% by weight) Boiling point range (C) Paraffins C6 - C12 0.1 - 20 69 - 230 C13 - C25 0+ - 10 230 - 450 C6 - C12 5 - 30 70 - 230 C13 - C23 5 - 30 230 - 405 C6 - C11, Mono- and dicyclic 0-5 80 -240 C12 - C18, Polycyclic 0+ - 5 240 - 400 C9 - C25 5 - 30 180 - 400 10 - 70 > 400 Cycloparaffins Aromatic Naphthenoaromatic Residual, including heterocycles After Moore et al., 1973 SOLUBILITY OF PETROLEUM HYDROCARBONS IN WATER Various components of petroleum are soluble in water to different degrees. More data are available on the solubility of hydrocarbons in distilled water than in sea-water. For those substances where data is available in both distilled and sea-water, the solubility of the hydrocarbons in sea-water is less than in distilled water. Petroleum 1, slide 26 here Table 15 - 4 lists the solubility of selected normal alkanes. Generally, the longer the hydrocarbon chain, the less soluble the hydrocarbon, although many irregularities exist. 7 Environmental Geochemistry, GLY 4241/5243, © David Warburton, 2015 Table 15 - 4 Solubilities of n-alkanes in Water Compound Number of Carbon Atoms Solubility in Distilled Water (ppm) Methane 1 24 Ethane 2 60 Propane 3 62 n-Butane 4 61 n-Pentane 5 39 n-Hexane 6 9.5 n-Heptane 7 2.9 n-Octane 8 0.66 n-Nonane 9 0.220 n-Decane 10 0.052 n-Undecane 11 0.0041 n-Dodecane 12 0.0037 0.0029 n-Tetradecane 14 0.0022 0.0017 n-Hexadecane 16 0.0009 0.0004 n-Octadecane 18 0.0021 0.0008 n-Eicosane 20 0.0019 0.0008 n-Hexacosane 26 0.0017 0.0001 n-Triacontane 30 0.002 n-Heptacontane 37 10-8 * * Extrapolated; Data after Clark and MacLeod, 1977 Petroleum 1, slide 27 here 8 Solubility in SeaWater (ppm) Environmental Geochemistry, GLY 4241/5243, © David Warburton, 2015 Table 15 - 5 presents solubility data for branched or isoalkanes. The isoalkanes are all more soluble than n-hexane, which has the same number of carbon atoms. 2,2-dimethylbutane, a compound with two branches, is about twice as soluble as n-hexane. Generally, branching increases solubility. The designation 2, 3, etc. shows the number of the carbon atom that the branch is attached to, starting from the end of the chain nearest the first branch. Table 15 - 5 Solubility of Isoalkanes in Distilled Water Compound Number of Carbon Atoms Solubility in Distilled Water (ppm) 2-Methylpentane 6 13.8 3-Methylpentane 6 12.8 2,2-Dimethylbutane 6 18.4 Data after Clark and MacLeod, 1977 Petroleum 1, slide 28 here The cycloparaffins are much more soluble than the alkanes. Table 15 - 6 presents solubility data for cycloparaffins. Like the alkanes, the cycloparaffins show decreasing solubility with increasing carbon number. However, the rate of solubility decrease is less for the cycloparaffins than for the alkanes. For example, cyclopentane is about four times more soluble than pentane, but cyclooctane is twelve times as soluble as n-octane. Aromatics, cyclic compounds with delocalized electrons shared around the ring, are the most soluble components of crude petroleum by far. Table 15 - 6 Solubility of Cycloparaffins in Distilled Water Compound Number of Carbon Atoms Solubility in Distilled Water (ppm) Cyclopentane 5 156 Cyclohexane 6 55 Cycloheptane 7 30 Cyclooctane 8 7.9 Data after Clark and MacLeod, 1977 Petroleum 1, slide 29 here Table 15 - 7 lists the solubilities of several aromatic compounds. Benzene, the simplest aromatic compound, is nearly 200 times more soluble than n-hexane. As with the other hydrocarbons, 9 Environmental Geochemistry, GLY 4241/5243, © David Warburton, 2015 solubility decreases as the carbon number increases, but this is complicated by branching, double ring structure, etc. For example toluene has less than a third of the solubility of benzene. Toluene has one methyl group substituted for a hydrogen atom attached to the ring. O-Xylene, which has two methyl groups attached next to each other on the benzene ring, has about one-third the solubility of toluene. Ethylbenzene, which has an ethyl group substituted for a hydrogen atom on the benzene ring, is slightly less soluble than o-xylene, although it has the same number of carbon atoms. It is much less soluble than toluene, with a methyl group instead of an ethyl group. Iso-Propylbenzene, with a propyl group attached to a benzene ring, is even less soluble. Thus, the longer the side chain attached to the aromatic compound, the less soluble it will be. Napthalene consists of two six-membered rings that have two carbon atoms common to both rings. Table 15 - 7 Solubility of Aromatics in Water Compound Number of Carbon Atoms Solubility in Distilled Water (ppm) Benzene 6 1780 Toluene 7 515 o-Xylene 8 175 Ethylbenzene 8 152 1,2,4-Trimethylbenzene 9 57 iso-Propylbenzene 9 50 Naphthalene 10 31.3 1-Methylnapthlene 11 25.8 2-Methylnapthlene 11 24.6 2-Ethylnapthlene 12 8.00 1,5-Dimethylnapthalene 12 2.74 2,3-Dimethylnapthalene 12 1.99 2,6-Dimethylnapthalene 12 1.30 Biphenyl 12 7.45 Acenapthalene 13 3.47 Phenanthrene 14 1.07 Anthracene 14 0.075 Chrysene 18 0.002 Data after Clark and MacLeod, 1977 10 Solubility in Seawater (ppm) 22.0 4.76 .71 Environmental Geochemistry, GLY 4241/5243, © David Warburton, 2015 Petroleum 1, slide 30 here In the naphthalene derivatives, the solubility again decreases with the presence and length of side chains. Biphenyl consists of two benzene rings linked by a single carbon-carbon bond. Of the five compounds with twelve carbon atoms, ethylnaphthalene (an ethyl group substituted for one hydrogen atom) is the most soluble. Biphenyl is next. Then the various dimethylnaphthalenes follow with decreasing solubility. The solubility in sea-water, where data is available, again indicate that most compounds are only about 60 - 70% as soluble in sea-water as in distilled water. Petroleum 1, slide 31 here To understand the solubility of petroleum hydrocarbons in water in a general way, we need to consider the nature of the substances involved. Water is composed of hydrogen and oxygen. The electronegativity of hydrogen is 2.1 and that of oxygen is 3.5, for a difference of 1.4. Pauling (1960) says that an electronegativity difference of 1.4 corresponds to bond with about 40% ionic character. Petroleum 1, slide 32 here Carbon has an electronegativity of 2.5. In hydrocarbons the electronegativity difference of 0.4 corresponds to about 5% ionic bond character. Water also has extensive hydrogen bonding. This accentuates the ionic bond character. Therefore, the bonds in water are strongly polar; the bonds in hydrocarbons are not. Petroleum 1, slide 33 here Shaw (1977) developed a hypothesis for the behavior of hydrocarbons in water. A hydrocarbon molecule in water may be regarded as a cavity in the structure of the water. Water molecules at the edge of the cavity are pulled away from the cavity by the strong hydrogen bonding between water molecules. This orders the water molecules near the cavity edge. The increase in order decreases entropy. The decrease in entropy means that energy must be supplied to the system to get hydrocarbons in solution. Thus, hydrocarbons are generally of low solubility in water. Indeed, hydrocarbons are thought of as hydrophobic. Petroleum 1, slide 34 here Hydrophobicity increases with increasing molecular weight and with increasing molar volume. Small, compact hydrocarbons are usually the most soluble. These same molecules are also volatile and are rapidly lost in most cases of petroleum spills. Heavier molecules with high molar volume are retained and are the most problematic in petroleum spills. 11 Environmental Geochemistry, GLY 4241/5243, © David Warburton, 2015 Petroleum 1, slide 35 here Although we are discussing primarily hydrocarbons, it should be noted that the solubility of hydrocarbons is greatly increased by the substitution of one or more polar functional groups for a hydrogen atom. For example, alcohols are compounds with a hydroxy group (-OH) substituted for hydrogen. The breakdown products (chemical, photochemical, and microbial) of petroleum hydrocarbons are often smaller or have polar functional groups attached. This means that the breakdown products are often of higher solubility than the original petroleum. Petroleum 1, slide 36 here The breakdown products with polar functional groups may act as natural dispersants. The polar functional group is hydrophilic. Compounds that contain both hydrophobia and hydrophilic regions may be called amphipathic (Robotham and Gill, 1989). Petroleum 1, slide 37 here Amphipathic molecules can bind to both water and hydrocarbons, thus making the hydrocarbons more soluble in water. Common chemical and biological breakdown products of petroleum hydrocarbons include the amphipathic substances acids, ketones, and quinones. Common biological breakdown products include long-chain alcohols and acids. All may act as dispersants. Petroleum 1, slide 38 here In addition anthropogenic dispersants exist. These include domestic and industrial detergents, and substances deliberately applied to petroleum spills to act as dispersants. Unfortunately, although dispersants may help to make a petroleum spill less visible, they often harm the environment more than the original spill. ENVIRONMENTAL SIGNIFICANCE OF DISSOLVED HYDROCARBONS Petroleum 1, slide 39 here Why should we be more concerned about dissolved hydrocarbons than emulsified, adsorbed, or complexed petroleum in water? Two papers claim that only in the dissolved form is petroleum acutely toxic (Landrum et al., 1985; McCarthy et al., 1985). When petroleum is absorbed or otherwise bound, the attraction is too strong to allow significant uptake by biological organisms (Robotham and Gill, 1989). Thus, the most soluble compounds are the most dangerous. 12 Environmental Geochemistry, GLY 4241/5243, © David Warburton, 2015 Petroleum 1, slide 40 here Traditionally the BTEX compounds are regarded as the most dangerous hydrocarbons. BTEX stands for benzene, toluene, ethylbenzene, and xylene. One reason these compounds are so dangerous is that they are significant components of refined petroleum products such as gasoline and jet fuel. Spills of gasoline or jet fuel in the marine or terrestrial environments may have severe consequences. Petroleum 1, slide 41 here Two short video interviews with Terri Tamminen, Author and Environmental Policy Advisor, about BTEX compounds in gasoline. Petroleum 1, slide 42 here A short video clip about sources and risks from benzene in the home. REFERENCES Robert C. Averett and Diane M. McKnight, Chemical Quality of Water and the Hydrologic Cycle, Lewis, Chelsea, Michigan, 1987. B.P. Statistical Review of World Energy, June 2016, https://www.bp.com/content/dam/bp/pdf/energy-economics/statistical-review-2016/bp-sta tistical-review-of-world-energy-2016-full-report.pdf, (last seen November 3, 2016). R.C. Clark and W.D. MacLeod, Inputs, Transports, and Concentrations, in Effects of Petroleum on Arctic and Subarctic Marine Environments and Organisms: Vol.1 Nature and Fate of Petroleum, edited by D.C. Malins, pp. 91-223, Academic Press, 1977. Energy Information Administration, Annual Energy Review, 2005, http://www.eia.doe.gov/emeu/aer/ , (last seen March 30, 2011). R.L. Hirsch, R. Bedzek and R. Wendling, Peaking of World Oil Production: Impacts, Mitigation, & Risk Management, last modified August 11, 2006, http://www.oilcrash.com/articles/hirsch.htm, (Last seen March 30, 2011). R.A. Horne, The Chemistry of Our Environment, Wiley-Interscience, New York, 1978. R.H. Hunt and M.J. O'Neal, Petroleum Composition, in Encyclopedia of Chemical Technology, second edition, edited by R.E. Kirk and D.F.Othmer, Vol. 14, John Wiley and Sons, New York, 1966. 13 Environmental Geochemistry, GLY 4241/5243, © David Warburton, 2015 Konrad B. Krauskopf, Introduction to Geochemistry, second edition, McGraw-Hill, New York, 1979. P.F. Landrum, M.D. Reinhold, S.R. Nihart, and B.J. Eadie, Predicting the bioavailability of organic xenobiotics to Pontoporeia hoyi in the presence of humic acid and fulvic materials and natural dissolved organic matter, Environmental Toxicology and Chemistry, 4, 459-467, 1985. J.F. McCarthy, B.D. Jiminez, and T. Barbee, Effect of Dissolved Humic Material on Accumulation of Polycyclic Aromatic Hydrocarbons: structure-activity relations, Aquatic Toxicology, 7, 15-24, 1985. S.F. Moore, R.L. Dwyer, and A.M. Katz, A Preliminary Assessment of the Environmental Vulnerability of Machias Bay, Maine to Supertankers, Massachusetts Institute of Technology, Cambridge, Massachusetts, 1973. Linus Pauling, The Nature of the Chemical Bond, third edition, Cornell University Press, Ithaca, New York, 1960. Robert Rapier, World Sets New Oil Production and Consumption Record. July 10, 2014, http://www.energytrendsinsider.com/2014/07/10/world-sets-new-oil-production-and-cons umption-records/ , (last seen October 26, 2014). D.G. Shaw, Hydrocarbons in the Water Environment, in Fate and Effects of Petroleum Hydrocarbons in Marine Ecosystems and Organisms, edited by D.A. Wolfe, pp. 8-18, Pergamon Press, 1977. J.G. Soussan, World Energy Picture, in Environmental Issues in the 1990's, edited by A.M. Mannion and S.R. Bowlby, John Wiley and Sons, New York, 1992. H. Stephen Stoker and Spencer L. Seager, Organic Chemical Pollution: Petroleum, Pesticides, and Detergents, in Environmental Chemistry, edited by J. O'M. Bockris, Plenum, New York, 1977. U.S. Energy Information Administration, U.S. Field Production of Crude Oil, Monthly, August, 2016, http://www.eia.gov/opendata/qb.cfm?sdid=PET.MCRFPUS1.M , (last seen November 3, 2016). 4241LN15_pp_F16.pdf November 3, 2016 14
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